45th International Conference on Environmental Systems ICES-2015-094 13-17 July 2015, Seattle, Washington International Space Station Environmental Control and Life Support System Mass and Crewtime Utilization In Comparison to a Long Duration Human Space Exploration Mission Robert M. Bagdigian 1 NASA Marshall Space Flight Center, Huntsville, Alabama 35812 Jason Dake 2 NASA Johnson Space Center, Houston, Texas, 77058 Gregory Gentry 3 and Matt Gault 4 The Boeing Company, Houston, TX 77058 Over the last two-and-a-half decades, the International Space Station’s (ISS) Environmental Control and Life Support System (ECLSS) has grown and evolved in size, complexity, and capability. The functions that it performs today are many of those that will need to be performed in the future aboard spacecraft and habitats that will enable long duration human exploration missions to destinations beyond low earth orbit. Regardless of the particular deep space destination, it is widely accepted that highly reliable ECLS systems that depend minimally on expendable equipment will be required. An important question, particularly in today’s fiscally- constrained environment, is how well suited is the ISS ECLSS suite of technologies to meeting the needs of future missions? To help begin answering this question, the maintenance history of the ISS Water Recovery and Oxygen Generation Systems has been surveyed. Equipment mass utilization rates, achieved hardware operating lifetimes, and crewtime spent on maintenance tasks have been tallied to provide a surrogate measure of reliability. These data are also compared to notional targets for a hypothetical three-year Mars mission. Nomenclature AES = Advanced Exploration Systems ARFTA = Advanced Recycle Filter Tank Assembly ATV = Automated Transfer Vehicle CDRA = Carbon Dioxide Removal Assembly CO2 = Carbon Dioxide CR = Catalytic Reactor ORU ECLS = Environmental Control and Life Support ECLSS = Environmental Control and Life Support System DA = Distillation Assembly DMSD = Dimethylsilanediol FCA = Firmware Controller Assembly FCPA = Fluids Control and Pump Assembly GS = Gas Separator ORU 1 Chief, Environmental Control and Life Support Development Branch, NASA Marshall Space Flight Center, Mailcode ES62, Huntsville, AL, 35812 2 International Space Station Environmental Control and Life Support System Manager, NASA Johnson Space Center, Mailcode EC3, Houston, TX 77058 3 International Space Station Environmental Control and Life Support Technical Lead, 3700 Bay Area Blvd, Mailstop HB2-40, Houston, TX 77058 4 International Space Station Logistics and Maintenance, 3700 Bay Area Blvd, Houston, TX 77058. H2 = Hydrogen H2 = Hydrogen ORU H2O = Water H2O = Water ORU ISS = International Space Station IX = Ion Exchange Bed ORU kg = kilogram MCV = Microbial Check Valve ORU MLS = Mostly Liquid Separator MTBF = Mean Time Between Failure N2 = Nitrogen ORU NASA = National Aeronautics and Space Administration O2 = Oxygen
16
Embed
International Space Station Environmental Control and Life ...
This document is posted to help you gain knowledge. Please leave a comment to let me know what you think about it! Share it to your friends and learn new things together.
Transcript
45th International Conference on Environmental Systems ICES-2015-094 13-17 July 2015, Seattle, Washington
International Space Station Environmental Control and Life
Support System Mass and Crewtime Utilization In
Comparison to a Long Duration Human Space Exploration
Mission
Robert M. Bagdigian1
NASA Marshall Space Flight Center, Huntsville, Alabama 35812
Jason Dake2
NASA Johnson Space Center, Houston, Texas, 77058
Gregory Gentry3 and Matt Gault4
The Boeing Company, Houston, TX 77058
Over the last two-and-a-half decades, the International Space Station’s (ISS) Environmental Control and
Life Support System (ECLSS) has grown and evolved in size, complexity, and capability. The functions that it
performs today are many of those that will need to be performed in the future aboard spacecraft and habitats
that will enable long duration human exploration missions to destinations beyond low earth orbit. Regardless
of the particular deep space destination, it is widely accepted that highly reliable ECLS systems that depend
minimally on expendable equipment will be required. An important question, particularly in today’s fiscally-
constrained environment, is how well suited is the ISS ECLSS suite of technologies to meeting the needs of
future missions? To help begin answering this question, the maintenance history of the ISS Water Recovery
and Oxygen Generation Systems has been surveyed. Equipment mass utilization rates, achieved hardware
operating lifetimes, and crewtime spent on maintenance tasks have been tallied to provide a surrogate measure
of reliability. These data are also compared to notional targets for a hypothetical three-year Mars mission.
Nomenclature
AES = Advanced Exploration Systems
ARFTA = Advanced Recycle Filter Tank Assembly
ATV = Automated Transfer Vehicle
CDRA = Carbon Dioxide Removal Assembly
CO2 = Carbon Dioxide
CR = Catalytic Reactor ORU
ECLS = Environmental Control and Life Support
ECLSS = Environmental Control and Life Support
System
DA = Distillation Assembly
DMSD = Dimethylsilanediol
FCA = Firmware Controller Assembly
FCPA = Fluids Control and Pump Assembly
GS = Gas Separator ORU
1 Chief, Environmental Control and Life Support Development Branch, NASA Marshall Space Flight Center,
Mailcode ES62, Huntsville, AL, 35812 2 International Space Station Environmental Control and Life Support System Manager, NASA Johnson Space Center,
Mailcode EC3, Houston, TX 77058 3 International Space Station Environmental Control and Life Support Technical Lead, 3700 Bay Area Blvd, Mailstop
HB2-40, Houston, TX 77058 4 International Space Station Logistics and Maintenance, 3700 Bay Area Blvd, Houston, TX 77058.
H2 = Hydrogen
H2 = Hydrogen ORU
H2O = Water
H2O = Water ORU
ISS = International Space Station
IX = Ion Exchange Bed ORU
kg = kilogram
MCV = Microbial Check Valve ORU
MLS = Mostly Liquid Separator
MTBF = Mean Time Between Failure
N2 = Nitrogen ORU
NASA = National Aeronautics and Space
Administration
O2 = Oxygen
International Conference on Environmental Systems
2
O2 = Oxygen ORU
OGA = Oxygen Generation Assembly
OGS = Oxygen Generation System
ORU = Orbital Replacement Unit
P = Pump ORU
PC = Process Controller ORU
PCPA = Pressure Control and Pump Assembly
psia = pounds per square inch absolute
PS = Pump Separator ORU
PSM = Power Supply Module
R&R = Removal and Replacement
RFTA = Recycle Filter Tank Assembly
RSA = Rotary Separator Accumulator
SF = Separator Filter ORU
SPA = Separator Plumbing Assembly
UPA = Urine Processor Assembly
USOS = United States Orbital Segment
WD = Water Delivery ORU
WPA = Water Processor Assembly
WRS = Water Recovery System
WS = Water Storage ORU
WSTA = Wastewater Storage Tank Assembly
WW = Wastewater ORU
I. Background
An important objective of the National Aeronautics and Space Administration (NASA) strategic plan1 is to
“expand human presence into the solar system and to the surface of Mars to advance exploration, science, innovation,
benefits to humanity, and international collaboration”. To meet this objective, NASA is identifying and assessing
mission concepts that can be combined into an evolvable campaign of progressively more demanding missions that
incrementally demonstrate capabilities that will be needed to enable human exploration of the Mars surface2. Success
in achieving demanding campaign objectives within fiscally-constrained environments will depend heavily on
focusing investments on filling capability gaps that can’t be filled with today’s state-of-the-art, flight-proven systems
and technologies. The International Space Station (ISS) environmental control and life support system (ECLSS)
performs many of the functions that are expected to be needed in vehicles and habitats supporting an evolvable Mars
campaign. Most likely, among those functions will be the need to reliably recycle oxygen and water in order to reduce
the mass and volume burdens placed on transportation systems. The ISS Oxygen Generation System (OGS) and
Water Recovery System (WRS) have been recycling oxygen and water since 2007 and 2008, respectively. Since
activation, in addition to enabling sustained ISS crew operations, these systems have been providing valuable insights
into the challenges with long duration oxygen and water recycling in an operational, human-occupied, spacecraft
environment. They are also providing a first glimpse into the readiness to proceed to the much bolder and challenging
step of sending humans to Mars and returning them safely. This paper provides an initial, top-level assessment of the
life cycle mass and maintenance time devoted to OGS and WRS, both of which provide a surrogate indication of
reliability, and compare hardware operating lifetimes achieved to date to a representative Mars mission scenario.
II. Mars Reference Missions
Two key mission characteristics that largely determine the ECLSS capabilities that will be needed are the total
amount of time that a crew will need to be supported and whether that support will need to be provided in a micro-
gravity or reduced-gravity (surface) environment3. Strongly influencing the manner by which those capabilities can
be provided are the typical constraints on mass, volume, power, combined with unique deep-space exploration realities
that prevent quick crew return to earth in emergency situations4. These characteristics and constraints are described
for a number of candidate Mars exploration mission concepts in the Mars Design Reference Architecture (DRA) 5.0,
the latest in a series of NASA Mars reference missions5. Although it does not represent a formal plan for the human
exploration of Mars, DRA 5.0 does provide a vision of potential approaches of how various exploration systems could
be used to implement the first human landing on Mars. In-space transportation capabilities combined with Earth-Mars
alignment phasing yield Mars mission profiles that are generally grouped into two distinct classes of potential round-
trip Mars missions: opposition-class missions, which are also commonly referred to a short-stay missions, and
conjunction-class missions, referred to as long-stay missions.
Short-stay, opposition-class missions are typified by relatively short duration stays (typically 30 to 60 days) on
Mars and one relatively long transit leg (either outbound to Mars or inbound back to Earth). As a class, they generally
have the highest propulsive energy requirements. A working timeline presented in DRA 5.0 for an opposition-class
mission includes an outbound crew transit of 174 days, a crew stay on the surface of Mars of 60 days, and a return
crew transit of 400 days. An important characteristic of such a mission, particularly with respect to ECLSS, is its
combined 574 days of crew time spent transiting to and from earth in the micro-gravity environment of deep space.
Alternatively, short-stay missions which substitute 60 days of orbital exploration of the Mars moons Deimos and
Phobos, would result in 634 days that crew members spend in a micro-gravity environment.
International Conference on Environmental Systems
3
Long-stay, conjunction-class missions are characterized by long-duration stay-times on Mars (as much as 550
days) and moderately-long transit times. As a class, conjunction missions require the lowest amounts of propulsive
energy. A working timeline for a conjunction class mission in DRA 5.0 includes 220-day outbound and return transit
legs separated by a 539-day Mars surface stay. Alternatively, crew could spend the entire stay-time engaged in the
orbital exploration of Deimos and Phobos, resulting in nearly 1000 days of crew time spent in micro-gravity.
Surface missions have two particular characteristics that can substantially influence the functions needing to be
provided by an ECLS system and the design of the system to perform those functions. The gravitational force on
Mars is roughly one-third that on Earth and would be sufficient to employ simpler techniques for phase separations
than the centrifugal and membrane-based diffusion techniques used in the micro-gravity environment on the ISS.
Gravitational forces on Phobos and Demos are roughly 1/1000th that on Earth and would likely require the same or
similar phase separation techniques employed on the ISS. The second surface characteristic is the potential availability
of in-situ resources from which useable oxygen and water could be extracted to meet crewmember metabolic needs.
In a Mars surface architecture in which in-situ resource utilization (ISRU) is used to produce oxygen for ascent stage
propulsion, the incremental amount of oxygen that would also be needed to support crew metabolic needs would be
relatively small in comparison, perhaps making it unnecessary for a Mars surface habitat located in the vicinity of an
ISRU-based propellant production plant to include its own oxygen recycling capability. Since the trade space for
ISRU applications in a Mars surface architecture remains large, the focus of this study has been limited to the micro-
gravity transit phase. This paper uses a cumulative 1000-days of crew support in a micro-gravity environment,
comparable to that envisioned in DRA 5.0 for a conjunction-class, orbital exploration of Phobos and Deimos, as the
basis for comparison to ISS WRS and OGS equipment capabilities.
III. International Space Station Maintenance Data
All on-orbit ISS maintenance activities are logged in the ISS Maintenance Data Collection. The collection
provides a record of scheduled and unscheduled maintenance activities associated with ISS hardware, typically linked
down to the maintainable item level and tracked by both part number and serial number. For WRS and OGS
equipment, this level of tracking typically equates to the ORU-level. For each maintenance activity, the scheduled
service or unscheduled discrepancy that triggered the activity is identified and the corresponding corrective action is
briefly described. Time (hours) spent or allocated to each activity is recorded separately for each crewmember that
participated in the activity for each day that the activity was in progress. Time includes that which was allocated for
procedure review, locating and collecting required equipment and tools, executing the procedure or activity, etc.
Maintenance methods are categorized as follows:
Removal and Replacement (R&R): The item being maintained is removed from its operational location within the
higher level system and replaced with a separate, functionally equivalent item. This method is typically used to
restore system functionality after a hardware item has failed unexpectedly or has reached the end of its operational
life.
Remove and Reinstall: The hardware being maintained is removed from its operational location within the higher
level system to facilitate crew member inspection or troubleshooting. Upon completion of the inspection or
troubleshooting, the hardware item is reinstalled into its original operating location and returned to service.
Repair: The hardware being maintained is either removed from its operational location or left in place while
crewmembers complete actions to repair (return to functional condition) the item. Upon completion of the repair,
the hardware item is returned to service.
Troubleshooting: Crewmembers perform investigative procedures intended to obtain information needed to
understand the cause(s) of anomalous performance and determine suitable corrective actions.
Inspection/Service: Crewmembers observe hardware items to obtain information needed to understand its current
condition or perform routine procedures needed to sustain the items’ proper functionality and performance and
protect it from a functional failure.
Cleaning: Crewmembers perform routine cleaning of hardware items (typically air filters) needed to sustain proper
system functionality and performance.
The ISS Maintenance Data Collection has been used as the reference data used throughout this study. Tabulated
crew-times that are reported in this paper reflect how the activities are recorded in the collection. In some cases, as
International Conference on Environmental Systems
4
the understanding of system operation and failures have evolved over the life the WRS and OGS, the categorization
of maintenance activities has also evolved accordingly. Since the intent of this study was to provide a high-level
survey of maintenance trends, rather than a detailed accounting of maintenance records, data in the collection has been
used as-is.
IV. International Space Station Water Recovery System
The International Space Station (ISS) Water Recovery System includes two main assemblies. The Urine Processor
Assembly (UPA) accepts pretreated urine collected from the crew and processes it through a vapor compression
distillation process. Distillate that is produced is combined with humidity condensate that is collected from the ISS
cabin atmosphere; the combined distillate and humidity condensate is then purified to potable water quality
specifications via the Water Processor Assembly (WPA) which, through a sequence of purification steps, purifies the
water to meet potable water quality specifications.
A simplified functional schematic of the UPA is shown in Figure 1. The UPA is packaged into seven Orbital
Replacement Units (ORUs). Pretreated urine is delivered to the UPA either from the United States Orbital Segment
(USOS) Waste and Hygiene Compartment (outfitted with a Russian urinal) or via manual transfer from the Russian
urine container (called an EDV). The urine is temporarily stored in the Wastewater Storage Tank Assembly (WSTA).
Figure 1. Urine Processor Assembly Schematic (through October 2011 shown on left, current shown on right)
The Fluids Control and Pump Assembly (FCPA) includes a four-tube peristaltic pump that moves urine from the
WSTA into the Distillation Assembly (DA), recycles the concentrated waste from the DA into the Advanced Recycle
Filter Tank Assembly (ARFTA) and back to the DA, and pumps distillate from the DA to the WPA. The DA is the
heart of the UPA, and consists of a rotating centrifuge where water is evaporated from the recirculated urine/brine at
low pressure. The vapor is compressed and subsequently condensed on the opposite side of the evaporator surface to
conserve latent energy. A rotary lobe compressor within the DA provides the driving force for the evaporation and
compression of water vapor. At the end of each brine concentration cycle, a crew member removes the ARFTA from
the rack and transfers the concentrated brine within it into a Russian EDV tank or Rodnik tank using a Russian
compressor and hose assembly for ultimate disposal. The ARFTA is then refilled with pretreated urine, which allows
the process to repeat. The ARFTA has less capacity (approximately 22 L) than the original 41 liter Recycle Filter Tank
Assembly (RFTA) which was manually removed by the crew and replaced with an empty assembly at the end of each
concentration cycle. The capability to fill and drain the ARFTA on ISS avoids the costly resupply penalty associated
with returning, ground-servicing, and re-launching each RFTA. The Pressure Control and Pump Assembly (PCPA)
includes another four-tube peristaltic pump which provides for the removal of non-condensable gases and water vapor
from the DA. Liquid cooling of the pump housing promotes condensation, thus reducing the required volumetric
capacity of the peristaltic pump. Gases and condensed water are pumped to the Separator Plumbing Assembly (SPA),
which recovers and returns water from the purge gases to the product water stream. A Firmware Controller Assembly
(FCA) provides the command control, excitation, monitoring, and data downlink for UPA sensors and effectors.
A simplified schematic of the WPA is provided in Figure 2. The WPA is packaged into 15 ORUs. Wastewater
composed of cabin humidity condensate, distillate from the UPA, and Sabatier product water is delivered to the WPA
and temporarily stored in a bellows tank within the Waste Water ORU (WW). The bellows maintains a slight positive
International Conference on Environmental Systems
5
pressure to push water and gas into the centrifugal Mostly Liquid Separator (MLS) within the Pump/Separator ORU
(PS). Gas is removed from the wastewater by the MLS and passes through the Separator Filter ORU (SF) where odor-
causing contaminants are removed from entrained air before its return to the cabin. Degassed water is pumped through
the Particulate Filter ORU (PF), followed by two Multifiltration Beds (MFB) where inorganic and non-volatile organic
contaminants are removed. The Sensor ORU (S) located between the two MFBs determines when the first bed is
saturated based on conductivity. At that point, the first MFB is removed, the second MFB is moved up to the first
position, and a fresh MFB is installed in the second position. Effluent from the second MFB enters the Catalytic
Reactor ORU (CR), where low molecular weight organics not removed by the MFB sorbents are oxidized in the
presence of oxygen, elevated temperature, and a catalyst. A regenerative heat exchanger recovers heat from the
catalytic reactor effluent water and returns it to the reactor’s inlet. The Gas Separator ORU (GS) removes excess
oxygen and gaseous oxidation by-products from the process water and returns it to the cabin. The Reactor Health
Sensor ORU (RHS) monitors the conductivity of the reactor effluent as an indication of whether the organic load
coming into the reactor is within the reactor’s oxidative capacity. Finally, the Ion Exchange bed ORU (IX) removes
dissolved products of oxidation and adds iodine for residual microbial control. The water is subsequently stored in
the Water Storage ORU (WS) and delivered on-demand to users via a pump and accumulator within Water Delivery
ORU (WD). The WPA is controlled by a process controller (PC) that provides the command control, excitation,
monitoring, and data downlink for WPA sensors and effectors. An Oxygen Filter ORU protects CR components from
particulates and a Microbial Check Valve ORU (MCV) protects product water from microbial contamination through
the WPA’s recycle line.
Figure 2. Water Processor Assembly Schematic
The logistical mass benefit of recycling water can be seen clearly in Figure 3 by comparing the mass of water
recycled to the mass of hardware that has been used to perform the recycling. The initial mass of the WRS when it
was launched in 2008 was 1385 kg (3048 lb). This mass includes the combined mass of all installed UPA and WPA
processing and storage tank ORUs, two process controllers, rack outfitting equipment (including an avionics air
assembly, rack power control module, and smoke detector assemblies), structure (including two standard ISS racks,
shelves, and brackets), and interconnecting cables and hoses. Through March 20, 2015 the system had produced
22,350 kg (49,170 b) of recycled potable water. Since the beginning of 2013, the average daily potable water
production rate has been approximately 12.7 kg/day (28 lb/day), corresponding roughly to a 3.4-person water
processing rate. Overall water recovery efficiency has been approximately 88%. Recycling this amount of potable
International Conference on Environmental Systems
6
water has required equipment to be replaced at various times due to failures, life limits being reached or exceeded, the
original logistical approach of returning UPA RFTAs to the ground for servicing, and the replacement of the fleet of
RFTAs with two ARFTAs in 2011. Since system activation, 2225 kg (4896 lb) of equipment has been replaced,
including 941 kg (2070 lb) in response to failures and 1284 kg (2826 lb) due to consumption of planned expendable
items such as UPA RFTAs, WPA MFBs, etc. The combined original system mass and the cumulative mass of
equipment that has since been replaced is 3608 kg (7938 lb). Normalizing this mass of hardware utilized with the
mass of water produced yields an overall equipment (original non-recurring system plus recurring replacements)
utilization mass of 0.16 kg of equipment per kg of water produced. The recurring portion of this mass utilization rate
is 0.10 kg of equipment per kg of water produced over the entire operating life of the WRS, and 0.08 kg of equipment
per kg of water produced since the UPA RFTAs were replaced with ARFTAs.
Figure 3. Water Recovery System Life Cycle Mass (through March 20, 2015)
In addition to impacting logistical mass, equipment failures and the need to periodically replace limited life and
expended ORUs have manifested themselves in the amount of crew time that has been dedicated to maintaining
WRS operability. The record of crew time applied to WRS is shown in Figure 4.
International Conference on Environmental Systems
7
Figure 4. Crew Time Applied to Water Recovery System Maintenance (through March 20, 2015)
In the nearly 6.5 years since activation, about 320 crew-hours have been recorded against WRS maintenance
tasks. When normalized against the water production data shown in Figure 3, this equates to approximately 14.3
crew-hours per 1000 kg (6.5 crew-hours per 1000 lb) of water recycled. Three quarters (247 crew-hours) were
dedicated to the removal and replacement of ORUs. The remaining quarter included tasks recorded as
troubleshooting (33 hours), repair (21 hours), inspection and servicing (16 hours), and removal and reinstallation (<1
hour).
Inspection of Figures 3 and 4 reveals some key information, much of which is being used by NASA to target
investments that will benefit the ISS program in the near-term and deep space missions in the longer term6,7. For
example, 36% of logistical mass and of crew time have been associated with the handling and disposal of urine
brine. Initial use of UPA RFTAs represents the largest WRS logistical mass (668 kg, 1470 lb), despite the fact that
their usage was curtailed in 2011 in lieu of ARFTAs. However, the logistics mass benefit of switching to ARFTAs
has come at the expense of crew-time, as crew efforts to remove and replace ARFTAs, drain their contents into
containers for disposal, and refill them with fresh pretreated urine are more frequent and involved than the effort to
remove and replace the higher-capacity RFTAs. The ISS program is implementing design changes to the WRS to
reduce crew time demands by enabling ARFTA servicing to be completed while installed in the rack. For
exploration missions, NASA is investing in candidate technologies to process urine brine in order to increase overall
water recovery beyond the 88% currently achieved on the ISS7. Crew time dedicated on ISS to disposing of brine
with ARFTAs could serve as a surrogate indicator for how much time might be need in exploration missions to
transfer brine to a processor, depending on the brine processing technology and system integration approach chosen.
The history of UPA and WPA ORU operating lives achieved since WRS activation is shown in histogram form
in Figures 5 through 8. For each ORU, a target operating life for each ORU is shown in black. The targets were
calculated based on supporting four crewmembers over the course of a 1000 day mission. Calculated targets also
assumed that humidity condensate and urine loads8 in an exploration transit vehicle, UPA and WPA processing
rates, and ORU duty cycles will all be comparable to those on ISS. It was also assumed that in a 1000-day
exploration mission in which outbound and return transit legs are separated by a prolonged period of surface
International Conference on Environmental Systems
8
exploration, expendable media items such as WPA Multifiltration Beds, Ion Exchange Bed, Particulate Filter, and
Microbial Check Valve would all be changed out prior to the return leg as part of a dormancy-management strategy.
Therefore, target lives for such expendable ORUs are assumed to be 500 days, whereas target lives for all other
electromechanical ORUs and controllers have been assumed to be 1000 days. In the histograms, the ISS predicted
life for each ORU (based on design and analysis) is shown in gray, and are labelled to indicate the basis for the
prediction (Mean Time Between Failure (MTBF) calculations, limited life component, or planned preventative
maintenance). Solid green bars represent ORUs that achieved service lives exceeding the corresponding mission
target life before being removed from service, while striped green bars indicate those that have exceeded the target
and were still in service at the time of this analysis. Solid and striped yellow bars represent ORUs that didn’t reach
the 1000 day target but for which there is reasonable confidence that the design is capable of doing so, according to
rationale discussed below. Solid and striped red bars represent ORUs that have fallen well short of the 1000 day
target.
Figure 5. UPA ORU Operating Life History Compared to a 1000-Day Mission Target Life
Of the UPA ORUs, all have achieved operating lives on the ISS that meet the 1000-day mission target life with
the exception of the FCPA. Repeated failures in the drive train linking the FCPA motor to the peristaltic pump head
have prevented any of the FCPA ORUs from achieving even half of a 1000-day target life. The same drive train
also failed in the second PCPA ORU. Development of a robust, alternative FCPA and PCPA drive train is among
the highest priority UPA design improvements that the ISS program is currently sponsoring9. The first two DA
ORUs were replaced due to failures, neither of which directly indicated a design shortcoming; the first DA failed
shortly after WRS activation due to wear induced on the ground from repeated assembly and disassembly of the
first-built unit, while the second DA failed due to calcium precipitation resulting from the unique chemistry of on-
orbit urine10. As part of the recovery from the calcium precipitation event, the first FCPA was replaced (along with
the second DA) as a precautionary measure even though it had not itself failed. As a result of this event, the ISS
program has developed an alternative urine pretreatment formulation intended to mitigate the formation of insoluble
salts at urine water recovery percentages up to 85%.11
International Conference on Environmental Systems
9
Of the 15 WPA ORUs, all have achieved the operating lives on the ISS that meet the 1000-day mission target
life with the exception of the Catalytic Reactor (CR) and Pump/Separator (PS). Catalytic reactor failures have all
been linked to leakage of water past o-ring seals located within the hot zones of the assembly. The ISS program has
funded design modifications to improve the sealing life in the elevated temperature environment as well as the
development of catalysts with high oxidation efficiency at lower operating temperatures which would benefit seal
durability9. The gear-style process pump within the PS ORU has failed on three separate occasions. During WPA
development, issues with the pump caused by wear of internal alumina oxide surfaces led to failures, particularly
following extended non-operating storage if the pump head was allowed to dry sufficiently to cause alumina oxide
debris to harden. The risk of lock-up following storage led to the ISS program sponsoring a modification of the
pump design to a “-2” configuration. Original “-1” pump heads were retained in the flight inventory with
procedures adopted to mitigate the risk of dryout-induced lockup during storage. The first two WPA PS on-orbit
failures occurred with the original “-1” configuration pump heads installed. Troubleshooting identified particulate
ingestion into the tightly-tolerance pump head as the cause of the first and second failures while hardened alumina
oxide prevented the third pump (“-2” configuration) from working at all. An External Filter Assembly (EFA) has
been added to the WPA upstream of the PS to protect the pump. To further protect against failures induced by solid
debris in wastewater, operation of the WPA has been modified to minimize large releases or solid biofilm or debris
from the wastewater storage tank bellows as it moves. A tightly-toleranced solenoid valve has been removed from
the flowstream, and. All remaining WPA PS ORUs include the “-2” configuration pump.
Although the WPA’s MFBs have exceeded the target life adopted in this assessment, bed replacements have
been forced by the periodic increases in potable water total organic carbon caused by dimethylsilanediol (DMSD)
migration through the WPA treatment train, rather than the saturation of MFB resins with ionic constituents per the
intended design approach12-14. Ground analyses of MFBs returned from orbit have indicated as much as 40% of
unused resin capacity remaining in the beds. Tests are currently underway9 to determine a more efficient
proportioning of resins and sorbents within the beds which, when combined with an alternate MFB changeout
strategy (that would allow initial ionic breakthrough constituents to pass to the downstream catalytic reactor) would
enable greater MFB service life for ISS or substantial reduction in MFB mass and volume for exploration.
Figure 6. WPA ORU Operating Life History Compared to a 1000-Day Mission Target Life (1 of 3)
International Conference on Environmental Systems
10
Figure 7. WPA ORU Operating Life History Compared to a 1000-Day Mission Target Life (2 of 3)
Figure 8. WPA ORU Operating Life History Compared to a 1000-Day Target Life (3 of 3)
V. International Space Station Oxygen Generation System
A simplified schematic of the OGA is shown in Figure 9. Feed water from the potable water bus enters the assembly
through the Water (H2O) ORU and flows through an Deionizing (DI) bed ORU, which serves to remove iodine and
coalesce gas bubbles that may be present in the feed water. If gas bubbles are detected by the gas sensor downstream
of the DI bed, the feed water is rejected to the waste water bus. The intent of this control strategy is to prevent any
International Conference on Environmental Systems
11
oxygen that may be present in the feed water from mixing with generated hydrogen. Water is electrolyzed into oxygen
and hydrogen in the Hydrogen ORU (H2), which contains the electrolysis cell stack. Oxygen produced by the cell
stack passes through the Oxygen Outlet ORU (O2) containing a water absorber, which protects the downstream
hydrogen sensors from liquid moisture. The Hydrogen Sensor ORU (H2S) monitors the product oxygen for the
presence of hydrogen, which would indicate a problem with the cell stack and signal the controller to shut down the
OGA. The Rotary Separator Accumulator (RSA) within the H2 ORU separates the product gaseous hydrogen from
the water which is re-circulated by the Pump ORU (P). The Nitrogen Purge ORU (N2) serves to purge system lines
upon shutdown with nitrogen. A resin bed (ACTEX-311) within the recirculation loop protects against the build-up
of harmful contaminants. The Process Controller ORU (PC) is responsible for OGA System command/control and
communication with the ISS command and data handling system. A dedicated Power Supply Module (PSM) provides
direct current to the electrolysis cell stack in proportion to the commanded oxygen production rate.
air assembly filters (4 crew-hours), and removal and reinstallation (2 crew-hours).
Inspections of Figures 10 and 11 indicate that nearly 50% of the OGS life cycle mass is accounted for by the
single changeout of the H2 ORU (125 kg, 275 lb) whereas crewtime has been dominated by the repetitive
replacement of the limited life H2 Sensor ORU (30 crew-hours, representing 21% of the total crewtime dedicated to
OGS). The ISS and Advanced Exploration Systems (AES) programs have been sponsoring efforts aimed at
reducing the mass impact associated with replacement of components (such as the cell stack) currently located
within the evacuated dome of the H2 ORU as well as alternative means to detect H2 leakage across cell membranes
that don’t rely on the current H2 Sensors with their relatively short calibration life15.
The history of OGA and PSM ORU operating lives achieved since OGS activation is shown in histogram form
in Figures 12 through 15. Of the 11 ORUs that make up the OGS, all have achieved operating lives on the ISS that
meet the 1000-day mission target life with the exception of the H2 Sensor ORU. The 150-day calibration life of the
current H2 Sensor falls well short of the 1000-day target established in this study for electromechanical devices that
would not be changed out prior to return as part of a dormancy management strategy. Even if the relatively small
size of the H2 Sensor ORU (approximately 10 lb, 4.5 kg) could justify it as a planned replacement item prior to
return, its calibration life today would still need to be extended by nearly a factor of 4 to enable such a strategy.
International Conference on Environmental Systems
14
Figure 12. OGA ORU Operating Life History Compared to 1000-Day Mission Target Life (1 of 3)
Figure 13. OGA ORU Operating Life History Compared to 1000-Day Mission Target Life (2 of 3)
International Conference on Environmental Systems
15
Figure 14. OGA ORU Operating Life History Compared to 1000-Day Mission Target Life (3 of 3)
Conclusions
Operation of the ISS WRS and OGS continues to provide informative data with which to begin assessing the
technological readiness to support future missions to Mars and its vicinity. With several readily apparent exceptions,
WRS and OGS equipment has been shown to be capable of achieving operational lifetimes on the order of those
needed to support such missions. It is important to note, however, that the sample size represented by the fleet of
WRS and OGS ORUs that have been used in operational service remains very small (sample size of 1 in most cases)
and that statistical reliability predictions cannot be supported by this data alone. Furthermore, other challenges likely
to be faced in developing Mars transit and surface vehicles, such as mass and volume constraints, water and oxygen
loop closure needed to support mission scenarios, dormancy management, equipment repairability, etc., also will need
to be considered as part of an integrated Mars exploration mission and vehicle design. But in terms of highlighting
first-order trends and focus areas needing improvements, the daily operation of the ISS WRS and OGS is providing
an invaluable first step towards human Mars exploration.
Acknowledgments
The authors wish to thank Mr. Richard Mason of United Technologies Aerospace Systems and Ms. Jennifer Pruitt
of the NASA Marshall Space Flight Center for their assistance with accessing and interpreting much of the on-orbit
ORU history data presented in this paper.
References 1 NASA Strategic Plan 2014, http://www.nasa.gov/sites/default/files/files/FY2014_NASA_SP_508c.pdf 2 Crusan, J., “Evolvable Mars Campaign”, http://www.nasa.gov/sites/default/files/files/NextSTEP-EMC-Reference.pdf 3 Metcalf, J., L. Peterson, R. Carrasquillo, and R. Bagdigian, “National Aeronautics and Space Administration Environmental
Control and Life Support Integrated Roadmap Development”, AIAA 2012-3444, 42nd International Conference on
Environmental Systems, San Diego, CA, 2012 4 Guirgis, P., W. West, M. Heldmann, D. Samplatsky, G. Gentry, and M. Duggan, “Beyond LEO: Life Support Requirements
and Technology Development Strategy”, ICES-2014-233, 44th International Conference on Environmental Systems, Tucson,
5 Drake, B.G., and K. D. Watts, editors, “Human Exploration of Mars Design Reference Architecture 5.0: Addendum #2”,
NASA/SP-2009-566-ADD2, March 2014. 6 Gatens, R.L., J.L. Broyan, A.V. Macatangay, J.L. Metcalf, S. Schull, and R.M. Bagdigian, “National Aeronautics and Space
Administration (NASA) Environmental Control and Life Support (ECLS) Technology Development and Maturation for
Exploration: 2013 to 2014 Overview”, ICES-2014-019, 44th International Conference on Environmental Systems, Tucson,
AZ, 2014. 7 Gatens, R.L., M.S. Anderson, J.L. Broyan, A.V. Macatangay, S.A. Shull, J.L. Perry, W.F. Schneider, and N.B. Toomarian,
“National Aeronautics and Space Administration (NASA) Environmental Control and Life Support (ECLS) Technology
Development and Maturation for Exploration: 2014 to 2015”, ICES-2015-111, 45th International Conference on
Environmental Systems, Bellevue, WA, 2015. 8 Tobias, B., J.D. Garr II, and M. Erne, “International Space Station Water Balance Operations,” International Conference on
Environmental Control Systems, July 2011. 9 Carter, D. L., J.M. Pruitt, R.M. Bagdigian, and M.J. Kayatin, “Upgrades to the International Space Station Water Recovery
System”, ICES-2015-133, 45th International Conference on Environmental Control Systems, Bellevue, WA, 2015. 10 Carter, D.L., “Status of the Regenerative ECLS Water Recovery System”, AIAA-2010-6216, 40th International Conference
on Environmental Systems, Barcelona, Spain, July 2010. 11 Carter, D.L., C. Brown, and N. Orozco, “Status of ISS Water Management and Recovery”, AIAA-2013-3509, 43rd
International Conference on Environmental Systems, Vail, CO, 2013. 12 Carter, D.L., B. Bowman, T. Rector, G. Gentry, and M. Wilson, “Investigation of DMSD Trend in the ISS Water Processor
Assembly”, AIAA 1563699, 43rd International Conference on Environmental Systems, Vail, CO, 2013. 13 Bowman, B., D.L. Carter, M. Wilson, H. Cole, N. Orozco, and D. Snowden, “Performance Evaluation of the ISS Water
Processor Multifiltration Beds”, AIAA 1277990, 42nd International Conference on Environmental Systems, San Diego, CA,
2012. 14 Bowman, B., D.L. Carter, J. Carpenter, N. Orozco, N. Weir, and M. Wilson, “Updated Performance Evaluation of the ISS
Water Processor Multifiltration Beds”, AIAA 1563679, 43rd International Conference on Environmental Systems, Vail, CO,
2013. 15 Takada, K.C., A.E. Ghariani, and S.Van Keuren, “Advancing the Oxygen Generation Assembly Design to Increase
Reliability and Reduce Costs for a Future Long Duration Mission”, ICES-2015-115, 45th International Conference on
Environmental Control Systems, Bellevue, WA, 2015.